Development and Application of Converter COMI-B Technology: A New Way of CO₂ Utilization

1. Introduction

The iron and steel industry is transitioning from high-speed to high-quality development, and the innovation capability of converter smelting technology has been continuously enhanced, realizing low-carbon, low energy consumption and clean smelting convertors, and contributing to the rapid development of green and low-carbon products [1,2,3,4]. The industrial sector accounts for 33% and 40% of global energy consumption and CO₂ emissions respectively, and the iron and steel industry contributes 33.8% of the industrial sector CO₂ emissions [5]. Blast furnace-converters constitute the main and longest production process generating approximately 1.9 tCO₂/t steel, and are worth considering in slowing down the carbon emission intensity. The capture and utilization of CO₂ is crucial [6].

Recently, the reduction of CO₂ emissions in the iron and steel industry has mainly involved three aspects: the upgrading of existing mature energy-saving technologies, the development and industrialization of key energy-saving technologies and the development and application of cutting-edge technologies [7,8]. Extensive studies on carbon emissions in the iron and steel industry have been conducted, mainly focusing on the use of CCS [9,10,11,12], CCU [13,14,15,16], and CCUS [17,18,19,20] to reduce carbon emissions. CCS technology includes three parts: carbon dioxide collection / capture, transportation, and storage, which focuses on storage after capture. Steeneveldt [21] pointed out that CCS depends on public acceptance and regulation of CO₂ storage, reduction of CO₂ capture costs, and adequate economic incentives. The difference between CCU and CCS is that CCU pays more attention to the utilization of CO₂ after capture. Research and application results show that CO₂ can be used in the chemical, agricultural and food industries, while the iron and steel industries can provide stable and clean CO₂ raw material gas, assisting in promoting the utilization path of CO₂ such as steel-chemical co-production and steel-agricultural carbon sequestration [22,23,24,25,26]. Valderrama introduced the preparation of oxalic acid and glycolic acid-based polyester materials from CO₂ and analyzed its application potential [27]. Zhang proposed a method for the synthesis of ethanol from CO₂, H₂, lignin, or various aryl methyl ethers derived from lignin [28]. Chang studied the feasibility of combining CO₂ capture with photobiological reactions (microalgae cells containing maximum spirulina) to remove some organic pollutants and nutrients from wastewater [29]. The capture and separation of CO₂ is the prerequisite for its storage and comprehensive utilization, and it is also the focus of the research [30,31,32].

Research on the application of CO₂ in the iron and steel industry has gradually increased in recent years. Owing to the gas characteristics, CO₂ can be used in high temperature processes such as blast furnace, converter, and refining. Here, we mainly study CO₂ resource utilization in a converter process. Researchers in the metallurgical field have conducted extensive research on converter top and bottom combined blowing oxygen, including the optimization of high efficiency oxygen supply of converter oxygen lance, converter bottom blowing layout and process optimization, etc., but there is limited research on the industrial application of converter top and bottom blowing CO₂ technology (COMI-B). One of the main research directions of the author of this study has been the application of CO₂ resources in converter steelmaking process for many years [33,34,35,36,37,38]. This study focused on experimental research on the application of COMI-B technology and converter smelting, and long-term industrial tests and applications were conducted. The participation of CO₂ in metallurgical reaction and its metallurgical advantages were verified.

2. Carbon dioxide utilization principle

2.1. Reaction mechanism

Based on metallurgical thermodynamics software and research literature, CO₂ is known to react with [C], [Si] and [Mn] in the molten pool in steelmaking temperature conditions, making it a weak oxidizing gas, as shown in Table 1.

Table 1 shows that both CO₂ and O₂ can react with the elements in the molten pool at steelmaking temperature, but there are two main differences between them when CO₂ participates in the high temperature characteristics of steelmaking: (1) Kinetics: CO₂ reacts with the elements in the molten pool to form CO gas, and 1 mol of CO₂ reacts with C in the molten pool to form 2 mol of CO gas, while O₂ only reacts with [C] to form CO gas and reacts with other elements to form compounds. Inert gases such as bottom blowing N₂ or Ar do not have bubble proliferation effect. The chemical reaction of CO₂ produces a large amount of CO gas, which has a bubble proliferation effect, helping to improve the stirring ability and kinetic conditions of the molten pool, and providing good kinetic conditions for dephosphorization, denitrification, and reduction of carbon and oxygen product. (2) Thermodynamics: Converter smelting is a process of oxidation heating, which is accompanied by a chemical reaction between O₂ and the elements in the molten pool to achieve continuous heating in the converter smelting process, but O₂ injection causes disorderly heating of the molten pool and iron evaporation to form a large amount of soot, which affects the dephosphorization efficiency and metal yield of converter smelting. The CO₂ decarbonization reaction is an endothermic reaction, and although the reaction with Si and Mn is exothermic, it is only about 30% exothermic relative to the reaction of O₂ with Si and Mn. The molten pool temperature can be controlled by injecting a certain proportion of CO₂, which provides optimum thermodynamic conditions for dephosphorization. According to the energy balance calculation, when 5–15% CO₂ is mixed into top-blown O₂, the temperature of the hot spot of the molten pool decreases by about 300–500 ℃, which will reduce the evaporation of metallic iron and consequently reduce the production of steelmaking dust and increase the metal yield.

2.2. CO₂ dephosphorization analysis

The dephosphorization reaction in the converter smelting process is a slag-steel interface reaction [39,40,41,42]. The degree of melting of slag and molten pool temperature in the early smelting stage (ES) have great influence on dephosphorization efficiency. Figure 1 shows the dephosphorization reaction between the elements in the molten pool and those in the slag at the slag-steel interface, which mainly includes the diffusion process of the reactants and products and the interfacial chemical reaction.

According to the viewpoint of slag molecular theory, the dephosphorization mechanism consists of the following reactions:

$$2\left[P\right]+5\left(FeO\right)+4\left(CaO\right)=\left(4CaO·P_2{O}_5\right)+5\left[Fe\right]$$

(1)

The dephosphorization efficiency can be calculated according to the dephosphorization Formula (2).

$$\lg \frac{(\%P)}{[\%P]}=\frac{12210}{T}-9.332+0.745\lg (\%T.Fe)+2.358\lg (\%CaO)$$

(2)

Formula (2) shows that effectively increasing K, FeO, and % CaO is beneficial to the dephosphorization reaction. Therefore, improving the basicity and oxidizability of slag and reducing the temperature of molten pool are beneficial to improve dephosphorization efficiency. A comprehensive analysis of the influence of CO₂ on dephosphorization in converter smelting indicated that CO₂ has weak oxidation characteristics, and the dephosphorization reaction formula is shown in Table 1. A large number of CO bubbles after reaction can help to improve the stirring of the molten pool and accelerate the melting of slag, and the reaction between CO₂ and C in the molten pool is endothermic, which can effectively control the heating rate of the molten pool by adjusting the amount of CO₂. Therefore, CO₂ is beneficial for converter dephosphorization.

2.3. CO₂ denitrification analysis

The main limiting steps of nitrogen removal from molten steel are as follows: (1) collision of [N] atoms, (2) combination of [N] atoms to form N₂, and (3) diffusion of N₂ to the interface. Under different conditions, the dissolution and escape of nitrogen is reversible. The solubility of N₂ in steel obeys the square root law. At a certain temperature, N₂ content dissolved in molten steel mainly depends on the partial pressure of N₂ in the furnace gas, as shown in formula (3).

$$\lg K_N=\lg \frac{\sqrt{P_{N_2}}}{[\%N]}=-\frac{518}{T}-1.063$$

(3)

where, K_N is the equilibrium constant; P_N2 is the partial pressure of nitrogen in the furnace gas, atm.

Removal of N becomes difficult if the [N] content at the end point of converter smelting is low. Further control of the [N] partial pressure in the molten pool reduces the [N] in molten steel [43,44]. CO₂ participates in converter smelting, and the proliferation effect of a large number of CO bubbles generated by CO₂ reaction not only provides optimum kinetic conditions for the molten pool, but also reduces the partial pressure of [N], which is beneficial for [N] removal from the molten pool. Figure 2 shows the [N] equilibrium values of temperature and N₂ partial pressure. The results show that increasing the bubble amount and decreasing the molten pool temperature are beneficial to the removal of [N]. Therefore, the addition of CO₂ is valuable to further reduce the N content in the molten pool.

2.4. Analysis of soot production in steelmaking

The supersonic oxygen jet contacts with the molten pool to form a high temperature fire zone in the converter smelting process, resulting in a large amount of molten iron evaporation that generates steelmaking dust, increasing the energy consumption and cost of pollutant treatment. The formation mechanism of steelmaking soot includes two models: the evaporation theory and bubble theory, as shown in Figure 3. The high temperature fire zone of the molten pool causes a large amount of metal iron to evaporate and oxidize. In the evaporation theory, when leaving the surface of the molten pool, part of the iron vapor is first oxidized and evolves into a nucleation core, and the rest of the iron vapor is gradually oxidized and grows in the rising process . In the bubble theory, a large number of CO bubbles float up during the molten pool decarburization reaction. When the bubbles break through the slag layer, surface potential energy is released and a small amount of metal iron and slag droplets spatter are produced through oxidation condensation. The formation mechanism affects the morphology and composition of soot. The soot particles formed by the evaporation theory are larger and relatively regular, while those formed by the bubble theory are finer and smaller with complex morphology.

3. Industrial tests

The content of this study is based on the industrial test data of COMI-B technology in a 120 t converter. The converter top blowing uses 4-hole oxygen lance nozzles with an outer diameter of 273 mm, average oxygen supply time of 12.5–13.5 min, gas supply intensity of top blowing O₂ and CO₂ of 3.5–4.1 Nm³/ (min∙t), and the mixing ratio of CO₂ is 4% CO₂ 15%. Four elements were installed in the converter bottom blowing and distributed on the 0.6 D indexing circle. An asymmetrical arrangement was adopted and N₂, Ar, or CO₂ were blown at the bottom during the test. Different bottom blowing modes were set according to different smelting steels. The average air supply intensity was 0.03–0.07 Nm³/ (min t). The industrial test of 120 t converter COMI-B technology was conducted, and a total of 400 furnace industrial tests were undertaken. The technological process is shown in Figure 4, according to the comparative analysis of the smelting indexes of different converters.

3.1. Material conditions

The raw material conditions are shown in Table 2, in which the average amount of hot metal is 108.8 t, and the amount and proportion of scrap is 26.7 t and 19.7 %, respectively. A small amount of pig iron was added to some furnaces during the industrial test, to achieve the converter smelting heat balance, and its composition is listed in Table 2.

The slagging agent and coolant data added in the industrial test process are shown in Table 3. The slagging agent consisted of lime, light burning and raw dolomite, the coolant mainly consisted of limestone, ore and sludge balls. The slagging agent was divided into two portions that were added separately and the coolant was added all at once within 80 % of the oxygen supply time, as it cannot not be added in the later stage of smelting.

3.2. Injection mode

The industrial test CO₂ was stably supplied by the gas source station, with a CO₂ gas content of more than 99.5 %. The CO₂ gas source pressure and flow rate were 2.0 MPa and 7000 Nm³/h, respectively, thus realizing the continuous and stable development of the industrial test process. To compare the metallurgical effect of the conventional and test furnaces, CO₂ mixing flow rate of the oxygen lance top blowing was dynamically adjusted with oxygen cumulative consumption. The converter smelting process was divided into early (ES), middle (MS) and late (LS) smelting stages. The stage is outlined in detail in Table 4.

Based on the converter smelting process conditions, the CO₂ mixing ratio is adjusted dynamically by stages, the flow rates in the ES, MS, and LS stages were 2300–3500 Nm³, 1400–2600 Nm³, and 2100–2800Nm³/h, respectively, divided into two top-blown O₂ + CO₂ modes. The original bottom blowing element was used in the test furnace, and the bottom blowing intensity was 0.03–0.07 Nm³/ (min∙t). The bottom blowing medium automatically switched N₂, Ar, CO₂, or CO₂ mixture according to the type of steel. Two CO₂ gas supply modes were designed in the industrial experiment, in which the total CO₂ consumption of Mode-1 was 209 Nm³ and that of Mode-2 was 176 nm. The CO₂ mixing ratio of Mode-1 was higher than that of Mode-2 in the ES stage, whereas it was the same in the MS and LS stages. In this study, the smelting effects of different gas supply modes of conventional furnace (N-Mode), Mode-1, and Mode-2 were compared. The main smelting steels in the test stage were low-carbon steel Q195Y and Q195L, and some medium and high carbon steel HRB400.

3.3. Experimental statistics and analysis

During the industrial test, the end point composition of molten steel consisting of O₂, N and slag in N-Mode, Mode-1, and Mode-2 were selected to calculate the gas recovery and soot production. The recovery amount of converter gas and the production of smoke and dust were determined from the statistical data of the smelting system, and the consumption of iron and steel was calculated based on the addition of molten iron, scrap, pig iron, and tapping in the converter. The end point compositions of molten steel, consisting of [O], [N], and slag were taken from slag and steel samples before tapping of the converter, and the end point slag composition and molten steel composition were analyzed by fluorescence analysis and spectrometry.

4. Analysis and discussion of laboratory research and industrial test results

Based on the industrial test data of N-Mode, Mode-1, and Mode-2 models, the metallurgical effects of COMI-B technology applied to the 120t converter are compared and analyzed. The changes of converter dephosphorization efficiency, slag composition, [C] and [O] accumulation and end point [N] content of molten steel, gas recovery, and soot production are analyzed.

4.1. Dephosphorization efficiency

Here, the study of CO₂ dephosphorization efficiency is based on the theoretical calculation and experimental research of FactSage thermodynamic software. Figure 5 shows dephosphorization efficiency changes of a high temperature experimental tube furnace and different CO₂ proportions. A double platinum rhodium thermocouple is arranged at the bottom of the crucible and connected with a thyristor temperature controller, which can be used for continuous temperature measurement and control. CO₂ and O₂ are injected into the furnace from the top of the tubular furnace through the quartz tube, and Ar is injected from the bottom to protect the atmosphere in the furnace tube and crucible. As shown in Table 1, CO₂ can react with phosphorus in the molten pool at 1573 K. With the progress of the smelting process, the phosphorus content in the molten pool shows a downward trend, and the dephosphorization efficiency is the highest when the mixing ratio of CO₂ is 25%. After 5 min in the ES, Si and Mn are largely oxidized, and the dephosphorization rate increases significantly. From 5 to 10 min, the change of dephosphorization rate with the ratio of CO₂ is small, indicating that under high phosphorus content in the molten pool, when the basicity, oxidizability, and temperature of the dephosphorization slag meet the dephosphorization requirements, the dephosphorization reaction is rapid and its rate is high. The dephosphorization rate with the CO₂ mixing ratio of 25 % is still high, indicating that the appropriate CO₂ mixing ratio can improve the dephosphorization efficiency.

Figure 6 shows the end point phosphorus content and dephosphorization effect of 120 t converter industrial test. The results show that the P content of molten steel with Mode-1 and Mode-2 is 0.0194 % and 0.0184 % respectively, which is 0.0006 % and 0.0016 % lower than that of N-Mode, and the dephosphorization efficiency is 4.2 % and 2.4 % respectively, which are higher than that of N-Mode, indicating that the dephosphorization efficiency of molten steel using COMI-B technology is higher, and the dephosphorization efficiency of Mode-1 is the highest. It also shows that the appropriate CO₂ mixing ratio is more beneficial to the dephosphorization reaction. The results shown in Figure 6 align to data in Table 1. CO₂ is known to react with C elements in the molten pool to absorb heat, and injecting a certain proportion of CO₂ can reduce the rate of temperature increase of the molten pool, providing optimum thermodynamic conditions for dephosphorization. At the same time, bottom blowing CO₂ reacts with the elements in the molten pool to form CO bubbles, which has a bubble proliferation effect, helping improve the kinetic conditions of the molten pool. The reaction characteristics of CO₂ are beneficial to improve dephosphorization efficiency. In addition, an appropriate CO₂ injection ratio will help form high alkalinity slag in the ES stage, and further improve the dephosphorization efficiency. The addition of CO₂ is conducive to the efficient and stable production of low phosphorus steel.

4.2. Slag composition and carbon and oxygen deposition of molten steel

Figure 7 shows the effect of varying [C] content on the decarburization rate of injection CO₂. The results show that with [C] content increase in molten steel, the decarburization rate of CO₂ continues to increase, but when the [C] content gets close to 1%, the decarburization rate of CO₂ is not enhanced and remains at a high level. The addition of CO₂ can reduce the oxidizability of the slag and [C] and [O] accumulation of molten steel because CO₂ can still achieve the decarburization effect in the converter during LS. Furthermore, although the amount of CO bubbles produced is less than that in the MS, the bubble volume is larger in the bottom blowing inert gas strengthening the stirring ability of the molten pool and the reaction area between steel and slag becomes larger and more sufficient. The O₂ diffusion rate from molten steel to slag increases and the oxidizability of the slag simultaneously decreases.

The influence of COMI-B technology on the composition of converter end slag is analyzed based on the test data. Figure 8 shows the changes of end-point slag composition under different modes. The results show that the mass fraction of end-point slag (FeO) in N-Mode, Mode-1, and Mode-2 is 18.38 %, 16.82 % and 16.34 %, respectively. The slag (FeO) content of Mode-1 and Mode-2 decreased by 1.56 % and 2.04 %, respectively, compared with the content of N-Mode. The results also show that the basicity of slag in N-Mode, Mode-1, and Mode-2 is 2.98, 3.09, and 3.23, respectively. Compared with the N-Mode model, the slag alkalinity of Mode-l and Mode-2 is 0.11 and 0.25 higher, respectively. Figure 8 shows that the main reason for this result is that CO₂ reacts with various elements in the molten pool to form CO, which enhances the stirring of the molten pool, promotes the reaction at the slag-gold interface, reduces the oxidizability in the slag, and increases the metal yield.

The value of the end-point carbon-oxygen product of molten steel not only represents the degree of peroxidation of molten steel, but also affects the yield of alloy and cleanliness of molten steel. Figure 9 shows the change in the end-point carbon-oxygen product of molten steel under different mode conditions. The results show that the end-point [C] and [O] product of molten steel in N-Mode, Mode-1, and Mode-2 is 28.98 × 10^-4, 27.61 × 10^-4, and 28.61 × 10^-4 respectively. Compared with N-Mode mode, the end-point carbon and oxygen product of molten steel in Mode-2 and N-Mode is 1.37 × 10^-4 and 0.37 × 10^-4, respectively. The decrease in the end-point carbon-oxygen product of molten steel is mainly due to the chemical reaction between CO₂ and elements in the molten pool to form a large number of CO bubbles, which promotes the reaction area between molten steel and slag and increases the [O] diffusion rate from molten steel to slag.

4.3. Nitrogen content in molten steel

For many types of steel, [N] is a harmful impurity that reduces the toughness, welding, and other properties of the steel, and should be entirely removed from steel [45,46]. The [N] in molten steel mainly originates from transferred metal material, slagging agent, air, and blowing gas medium. Currently, the production of low [N] steel mainly involves switching between N₂ and Ar at the bottom or blowing Ar during the entire process. The speed control link of absorbing or precipitating N₂ from molten steel mainly includes three speed control links:

(1) the gas diffuses to the surface of molten steel:

According to the mass transfer theory, the reaction rate is as follows:

$$v_1=\frac{k_{N,g}}{RT}\cdot \frac{A}{V_m}\cdot (P_{N_2}-P_{N_2}^{*})$$

(4)

where, $k_{N,g}$ is the mass transfer coefficient of [N] in the gas phase, m/s; A is the reaction boundary area, m²; $V_m$ is the volume of molten steel, m³; $P_{N_2}$ is the partial pressure of N₂ molecules in the gas phase, Pa; $P_{N_2}^{*}$ is the partial pressure of N₂ molecules on the surface of molten steel, Pa.

(2) adsorption chemical reaction:

$$\begin{gathered} N_2^{*}\underset{K_{-}}{\overset{K_{+}}{\rightleftarrows }}2{[N]}^{*} \\ {v}_2=\frac{dw[N]}{dt}=\frac{A}{V_m}\cdot (K_{+}{P}_{N_2}^{*}-K_{-}w{[N]}^{*}{ }^2) \end{gathered}$$

(5)

where, $K_{+}$is the rate constant of nitrogen absorption reaction, $K_{-}$is the rate constant of denitrification reaction, and $w{[N]}^{*}$ is the nitrogen content on the bubble surface.

(3) the diffusion of gas atoms in the molten steel:

$$\begin{gathered} {[N]}^{*}\to [N] \\ {v}_3=\frac{dw[N]}{dt}=k_{N,l}\cdot \frac{A}{V_m}\cdot (w{[N]}^{*}-w[N]) \end{gathered}$$

(6)

where, $k_{N,l}$ is the mass transfer coefficient of [N] in the molten steel, and $w[N]$ is the nitrogen content in the molten steel.

After finishing the formula, the rate equation of absorbing or precipitating N₂ from molten steel is obtained, as shown in the following formula:

$$\frac{1}{w[N]}-\frac{1}{w{[N]}_0}=K_{-}\cdot \frac{A}{V_m}\cdot t$$

(7)

where, $w[N]$ is the nitrogen content in molten steel at t time, ppm; $w{[N]}_0$ is the nitrogen content in molten steel at initial time, ppm.

Draw with the left $\frac{1}{w[N]}-\frac{1}{w{[N]}_0}$ coordinate on the left side of the formula (7) and the Abscissa on the right side of the $\frac{A}{V_m}\cdot t$ circle, as shown in Figure 10. The rate constants of denitrification reaction in bottom blowing CO₂, O₂, and Ar are 1.15 m/s, 0.60 m/s, and 0.12 m/s, respectively. The denitrification rate constant in bottom blowing CO₂ is 1.9 and 9.6 times higher than that in bottom blowing O₂ and Ar, respectively. The reason is that a large number of CO bubbles are produced by bottom blowing CO₂, which improves the denitrification capacity. The CO bubbles produced by CO₂ reaction are dispersed in the molten pool, which can strengthen the stirring and make the bubbles discharge faster. Therefore, CO₂ can be used as a bottom blowing source for smelting ultra low nitrogen steel.

Figure 11 shows the change of end-point nitrogen content in molten steel under different mode conditions. The results show that the end point nitrogen content of molten steel in N-Mode, Mode-1, and Mode-2 is 32.41, 25.92, and 28.64 ppm respectively. Compared with Mode-2, the end N content of 6.49 and 3.77 ppm decreased by 20 and 11.6% respectively in N-Mode. Bottom blowing CO₂ produces more CO bubbles, which enhances the stirring and bubble adsorption in the molten pool and accelerates the removal efficiency of nitrogen from molten steel.

4.4. Gas recovery

The calorific value and recovery of converter gas is an important energy index in converter smelting. The physical heat of converter gas can be used for preheating recovered steam and chemical heat can be used for ladle baking. Gas production and composition can be predicted from the material and energy balance of converter smelting. The results show that the furnace gas volume and CO volume in the furnace gas increased significantly with the increase of CO₂ injection ratio (Figure 12). When the CO₂ injection ratio increased to 23.5 %, the furnace gas volume increased from 75.0 to 100.24 m³, and the CO volume in furnace gas increased from 65.82 to 90.87 Nm³, but the volume fraction of CO increased by only 2.90%.

Based on the industrial test data of CO₂ injection, the change in converter gas recovery under different mode conditions is analyzed. The results show that the per ton steel gas recovery of N-Mode, Mode-1, and Mode-2 is 141.16, 143.48, and 146.11 Nm ³ respectively. Compared with N-Mode, the per ton steel gas recovery capacity of Mode-2 increased by 2.32 Nm³ and 4.95 Nm³, in Mode-1 and Mode-2, respectively. The results also showed that the content of CO in Mode-1 was the highest, reaching 38.99 %, which increased by 1.38% compared with N-Mode. In order to analyze the comprehensive characterization of converter gas production and gas calorific value, the expression method of equivalent converter gas production is introduced. According to the ratio of CO content in Mode-1 and Mode-2 to CO content in N-Mode, the gas production compared with N-Mode model is calculated, and the mathematical expression is as follows:

$$V_{Te-C}=\frac{V_{Te}\times C_{Te}}{C_{Con}}$$

(8)

where, $V_{Te-C}$gas consumption is the equal calorific value of gas in Mode-1 and Mode-2 models relative to N-Mode models, Nm³/t; $V_{Te}$ is the actual gas production in Mode-1 and Mode-2 models, Nm³/t; $C_{Te}$ and $C_{Con}$ represents gas CO content in Mode-1, Mode-2, and N-Mode,%.

Based on the formula, the per ton steel gas recovery of Mode-1 and Mode-2 models is 148.74 Nm³ and 149.45 Nm³, respectively, compared with N-Mode mode, the ton steel gas recovery volume increased by 7.58 Nm³ and 8.29 Nm³, respectively, and the gas recovery volume increased by 5.4% and 5.9% respectively, as shown in Figure 13. The main reason for the increase of gas recovery and calorific value in the experimental mode is that CO₂ reacts with elements in the molten pool to form a large amount of CO, and 1 mol of CO₂ reacts with carbon in the molten pool to form 2 mol of CO, which realizes the common improvement of gas quality and quantity.

4.5. Soot production

The enhanced O₂ supply in converter smelting is the core process of modern steelmaking, and the supersonic oxygen jet forms a high temperature fire zone with the molten pool in the smelting process, whose temperature exceeds the boiling point of iron. Therefore, the steelmaking process forms a mixture containing a variety of discrete metal oxide particles due to iron evaporation, that is, steelmaking dust. The standard iron-carbon melt was prepared by melting industrial pure iron and high purity pig iron, and the hot experimental study on the mechanism of oxygen steelmaking soot was undertaken in 500 kg experimental converter, as shown in Figure 14. The reaction rate of C and O₂ in the molten pool and the changing process of the particle size, composition, and morphology of steelmaking dust during converter blowing are tracked. The results show that in the ES stage, the C and O₂ reaction is limited, and the soot and iron loss are mainly derived from the evaporation of a large amount of metallic iron caused by high temperature in the hot spot of the molten pool, while in the MS stage, a large number of CO bubbles are produced in the decarburization reaction, which aggravates the boiling of the molten pool and carries a large number of fine broken particles in the smoke. In the LS stage, with the decreased C content in the molten pool, the amount of CO bubbles produced by the decarburization reaction decreased sharply, and the soot and iron loss were mainly caused by iron evaporation.

Figure 15 shows the amount of dust produced by large particles under different mode conditions in the industrial test process. The results show that the production of large particle size dust per ton of steel in N-Mode, Mode-1, and Mode-2 is 2.24 kg/t, 2.07 kg/t, and 1.91 kg/t, respectively. Compared with Mode-2 and N-Mode, the production of 0.17 kg/t and 0.33 kg/t is reduced by 7.6% and 14.7%, respectively. Figure 15 shows that the main reason is that the top blowing mixture of CO₂ and O₂ absorbs heat by the reaction between CO₂ and C in the molten pool, which reduces the temperature of the fire zone and reduces the total amount of dust in steelmaking.

5. Conclusion

We studied the influence of COMI-B technology on converter smelting effect, analyzed the high temperature characteristics of CO₂ participating in converter smelting reaction, and established the principle of CO₂ on molten steel composition, energy recovery and pollutant reduction. Through laboratory research and industrial test results, that the utilization of CO₂ in converter smelting was verified, and the beneficial effects of COMI-B compared with N-mode can be summarized as follows:

• The COMI-B technology helps to improve the converter dephosphorization efficiency, the bubble proliferation effect, and cooling characteristics of top and bottom combined blowing CO₂, and the dephosphorization rate is increased by 4.2%.
• COMI-B technology helps to reduce the oxidizability of slag, oxidizability and N content of molten steel. The bubble proliferation effect of bottom blowing CO₂ increases the rate of deoxidation and denitrification and reduces the carbon-oxygen product and nitrogen content of slag (FeO), molten steel and nitrogen by 2.04%, 1.37 × 10⁻⁴ and 20%, respectively.
• The COMI-B technology helps to increase gas recovery and gas calorific value, top and bottom combined blowing CO₂ participates in the reaction to generate a large amount of CO gas, and 1 mol CO₂ produces 2 mol CO, which increases the recovery amount of gas with the same calorific value by 5.9%.
• The COMI-B technology helps to reduce the soot production in the smelting process, the top blowing CO₂ reduces the high temperature fire zone of the molten pool, reduces the amount of soot formed by the evaporation of molten iron, and reduces the large size soot content by 14.7%.

Based on many beneficial results obtained by CO₂ in converter smelting process, CO₂ can be used to produce a steel grade with high requirements for phosphorus and nitrogen content. CO₂ can help to improve the cleanliness and purification of molten steel, provide favorable conditions for the stable production of subsequent refining and continuous casting processes, and realize the resource utilization of CO₂. Only CO₂ tons of steel in converter process can be used more than 5 kg. The CO₂ utilization potential of COMI-B technology applied in iron and steel industry is more than 7.5 million tons of CO₂. The research content of this paper can provide a reference for the application of CO₂ in converter smelting.